Sullivantia hapemanii

(Coult. & Fisher) Coult.

Purpus' Sullivantia

G3Vulnerable Found in 3 roadless areas NatureServe Explorer →
G3VulnerableGlobal Rank
Identity
Unique IDELEMENT_GLOBAL.2.155276
Element CodePDSAX0X010
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicendemic to a single nation
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderRosales
FamilySaxifragaceae
GenusSullivantia
Other Common Names
Hapeman's coolwort (EN) Hapeman's Coolwort (EN)
Concept Reference
Kartesz, J.T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. 2nd edition. 2 vols. Timber Press, Portland, OR.
Taxonomic Comments
Distinct species including two varieties (vars. hapemanii and purpusii).
Conservation Status
Review Date1997-12-23
Change Date1993-06-16
Edition Date1988-02-25
Edition AuthorsMARRIOTT, H. (1988), rev. D. Gries (1997)
Range Extent20,000-2,500,000 square km (about 8000-1,000,000 square miles)
Number of Occurrences6 - 20
Rank Reasons
This species has a narrow ecological range and a limited global distribution. Sullivantia hapemanii (including vars. hapemanii and purpusii) is known from at least 62 occurrences in Wyoming, Montana, Idaho, and Colorado. Most occur in inaccessible areas and would probably be affected by changes in the water quality and flow.
Range Extent Comments
Globally this species is restricted to a few areas in the mountains of Wyoming, Montana, Idaho and Colorado; within this area the two varieties have distinctly different ranges.

Sullivantia hapemanii var. hapemanii occurs in the Bighorn Mountains, and Bighorn Canyon area of North-Central Wyoming and South-Central Montana; and disjunct sites in Wind River Canyon and on Casper Mountain in Wyoming. Additionally, a disjunct population of var. hapemanii occurs in the Middle Fork Salmon River drainage, in Central Idaho.

Sullivantia hapemanii var. purpusii occurs in Western Colorado in Garfield, Rio Blanco, Gunnison, Pitkin and Montrose counties. Most of the occurrences in Gunnison and Montrose counties are in the Black Canyon of the Gunnison.
Occurrences Comments
As of 1994, 22 populations of Sullivantia hapemanii var. hapemanii had been documented in Wyoming, and one in Montana. Reported 40 element occurrences of S. hapemanii var. purpusii (Susan Spackman, Colorado Natural Heritage Program, personal communication, December 1995).
Threat Impact Comments
No threats are known to be significant at this time. The species is well protected by its largely inaccessible habitat. Occurrences would probably be threatened by changes in water quality and flow; for example elevated water levels could flood occurrences, or conversely, upstream flow reductions or changes in ground water hydrology could make existing sites too dry. Removal of nearby trees could reduce needed shade, and increase soil erosion (Fertig 1993). Human trampling from hiking or rock climbing poses a threat to the few accessible occurrences. Destruction of the cliffs it grows on could destroy occurrences, but this type of disturbance appears unlikely (Nyborg 1979).
Ecology & Habitat

Description

Sullivantia hapemanii is a perennial herb with erect, glandular to hairy stems which stand 5-60 cm high. The basal leaves have petioles (stalks) which are usually much longer than the blades; the blades are 1-11 cm wide and kidney to circular shaped with 5-13 palmate lobes and sharply toothed margins. The few stem leaves are alternate, smaller than the basal leaves, and have short petioles. The flowers are borne in a glandular inflorescence with long spreading branches. The calyx is green, 1.5-3 mm long, and is bell-shaped with 5 triangular lobes. There are 5 separate white petals which are 1.2-5 mm long and are broad spatula-shaped and narrowed at the base. There are 5 short stamens and a single pistil which is about 1/2 buried in the hypanthium. The fruit is a dry, 2-celled, multi-seeded capsule, with axil placentation.

The two varieties can be distinguished by measurable differences in the appearance of the ovary at anthesis and mature fruiting capsules. In var. hapemanii the ovary is about as long as it is wide; while in var. purpusii the ovary is usually about twice as long as it is wide. The fruit of var. hapemanii is an ovate cylindrical capsule less than 2.5 times (usually ca 2 times)longer than broad at maturity.; in contrast the fruit of var. purpusii is long and cylindrical, and is very narrow in relation to its width, at least 2.5 times longer than broad at maturity (Soltis 1991).

Diagnostic Characteristics

This is the only species of its genus in Montana. It is distinguished from other members of the Saxifrage family by having flowers with 5 stamens, a 2-celled ovary with axil placentation, and the calyx and petal dimensions of 1.5-3 mm and 1.2-5 mm, respectively. White flowers, five stamens, an open and erect inflorescence usually with branches perpendicular to stem, and lobed basal leaves with entire or erose margins distinguish var. hapemanii from other similar species in its range (Fertig 1993).

Habitat

This species is found in moist-wet locations, such as moist cliffs near water, usually in association with calcareous rock outcrops.

Var. hapemanii is found scattered throughout mesic limestone/dolomite canyons from 3,700 to 7,400 feet in elevation, on various aspects and slopes ranging from 0 - 90 degrees, in association with ferns and mosses. In Wyoming, it is restricted to moist - wet calcareous outcrops and boulders along streams and, generally, in well-shaded places, and sites appear to be dependent on high moisture or humidity (Fertig 1993). On the Bighorn National Forest, many, but not all, of the populations are found on mossy substrate (Michele Girard, personal communication, November 1995). However several occurrences have recently been recently observed in dry canyons and canyons with intermittent streams (personal observation). In Idaho, Bob Moseley reports that var. hapemanii has been found on wet granite outcrops associated with waterfalls or dripping water (Fertig 1993).

Var. purpusii is found "in very specialized habitat" such as wet dripping cliffs, moist canyon walls and in close proximity to waterfalls, (Soltis 1991), and on overhangs, permanently wet cracks and crevices, and on Northeast to Northwest slopes or microsites at elevations ranging from 6,500 to 10,000 feet, sometimes associated with a rare columbine (aquilegia barnebyi)(Nyborg 1979). It is found growing on limestone, shale, and quartzite cliffs (Susan Spackman, Colorado Natural Heritage Program, personal communication, December 1995).

Ecology

Population/occurrence size is highly variable; in some areas in Wyoming var. hapemanii occurs as isolated patches (subpopulations) of several to several thousand; (Marriot & Jones 1989).

Reproduction is by seed; the species is not stoloniferous (Soltis 1991). Var. hapemanii plants flower and fruit from June to August, with fruiting sometimes continuing to mid-September (Fertig 1993). Var. purpusii flowers from mid June to late July, and fruits from July to August.
Other Nations (1)
United StatesN3
ProvinceRankNative
MontanaS2Yes
ColoradoS3Yes
IdahoS2Yes
WyomingS3Yes
Plant Characteristics
Economic Value (Genus)No
Roadless Areas (3)
Wyoming (3)
AreaForestAcres
Cloud Peak ContiguousBighorn National Forest113,757
Leigh CreekBighorn National Forest19,180
Little BighornBighorn National Forest133,949
References (10)
  1. Fertig, W. 1993. Field survey for Cleome mulitcaulis, Cymopterus williamsii, and Sullivantia hapemanii in north-central Wyoming. Unpublished report prepared for the Bur. of Land Management, Casper District by the Wyoming Natural Diversity Database, Laramie.
  2. Flora of North America Editorial Committee (FNA). 2009. Flora of North America north of Mexico. Vol. 8. Magnoliophyta: Paeoniaceae to Ericaceae. Oxford University Press, New York. xxiv + 585 pp.
  3. Idaho Native Plant Society. 1993. Federal candidate (C1 and C2) and listed rare plants of Idaho. unpaginated.
  4. Kartesz, J.T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. 2nd edition. 2 vols. Timber Press, Portland, OR.
  5. Nyborg, Gerald W. 1979. Grand Mesa, Uncompahgre, and Gunnison National Forests management plan for proposed endangered species.
  6. Soltis, D. E. 1980. Flavonoids of SULLIVANTIA: Taxonomic implications at the generic level with the Saxifraginae. Biochemical Systematics and Ecology 8:149-151.
  7. Soltis, D. E. 1981. Variation in hybrid fertility among the disjunct populations and species of SULLIVANTIA (Saxifragaceae). Canadian Journal of Botany 59:1174-1180.
  8. Soltis, D. E. 1982. Heterochromatin banding in BOYKINIA, HEUCHERA, MITELLA, SULLIVANTIA, TIARELLA, and TOLMIEA (Saxifragaceae). American Journal of Botany 69(1):108-115.
  9. Soltis, D.E. 1991. A revision of <i>Sullivantia </i>(Saxifragaceae). Brittonia 43(1): 27-53.
  10. Weber, W.A., and R.C. Wittmann. 1996b. Colorado flora: Western slope. Univ. Press of Colorado, Niwot, Colorado. 496 pp.